Piet Wester

Tobacco smoke is a toxic and carcinogenic mixture of more than 5,000 chemicals. The present article provides a list of 98 hazardous smoke components, based on an extensive literature search for known smoke components and their human health inhalation risks. An electronic database of smoke components containing more than 2,200 entries was generated. Emission levels in mainstream smoke have been found for 542 of the components and a human inhalation risk value for 98 components. As components with potential carcinogenic, cardiovascular and respiratory effects have been included, the three major smoke-related causes of death are all covered by the list. Given that the currently used Hoffmann list of hazardous smoke components is based on data from the 1990s and only includes carcinogens, it is recommended that the current list of 98 hazardous components is used for regulatory purposes instead. To enable risk assessment of components not covered by this list, thresholds of toxicological concern (TTC) have been established from the inhalation risk values found: 0.0018 μg day(-1) for all risks, and 1.2 μg day(-1) for all risks excluding carcinogenicity, the latter being similar to previously reported inhalation TTCs.

Toxaphene production, in quantities similar to those of polychlorinated biphenyls, has resulted in high toxaphene levels in fish from the Great Lakes and in Arctic marine mammals (up to 10 and 16 microg g-1 lipid). Because of the large variabiliity in total toxaphene data, few reliable conclusions can be drawn about trends or geographic differences in toxaphene concentrations. New developments in mass spectrometric detection using either negative chemical ionization or electron impact modes as well as in multidimensional gas chromatography recently have led researchers to suggest congener-specific approaches. Recently, several nomenclature systems have been developed for toxaphene compounds. Although all systems have specific advantages and limitations, it is suggested that an international body such as the International Union of Pure and Applied Chemistry make an attempt to obtain uniformity in the literature. Toxicologic information on individual chlorobornanes is scarce, but some reports have recently appeared. Neurotoxic effects of toxaphene exposure such as those on behavior and learning have been reported. Technical toxaphene and some individual congeners were found to be weakly estrogenic in in vitro test systems; no evidence for endocrine effects in vivo has been reported. In vitro studies show technical toxaphene and toxaphene congeners to be mutagenic. However, in vivo studies have not shown genotoxicity; therefore, a nongenotoxic mechanism is proposed. Nevertheless, toxaphene is believed to present a potential carcinogenic risk to humans. Until now, only Germany has established a legal tolerance level for toxaphene--0.1 mg kg-1 wet weight for fish.

Adverse trends in the reproductive health of male fish, including testis abnormalities and intersex gonads, have been increasingly reported over recent years. These effects have been associated with the exposure of fish to natural, synthetic, and xenobiotic estrogens present in the aquatic environment. A novel in vivo test system using transgenic zebrafish has been developed to rapidly determine the effects of estrogenic chemicals on critical life stages and sensitive target organs in the fish. In the transgenic zebrafish, an estrogen binding sequence linked to a TATA box and luciferase reporter gene was stably introduced. Binding of a substance to endogenous estrogen receptors (ER) and the subsequent transactivation of the ER result in luciferase gene induction that is easily measured in tissue lysates. Exposure to estradiol (E2) during juvenile stages of the transgenic zebrafish revealed the period of gonad differentiation to be the most responsive early life stage. In adult male transgenic zebrafish, the testis was the most sensitive and responsive target tissue to estrogens. Partial sequences of zebrafish estrogen receptor subtypes α and β were cloned for the first time and were found to be differentially expressed in developing fish and tissues of adult male zebrafish. The transgenic zebrafish assay is a promising new tool to rapidly determine the estrogenic potency of chemicals in vivo.